首页 | 本学科首页   官方微博 | 高级检索  
相似文献
 共查询到20条相似文献,搜索用时 639 毫秒
1.

Goal and Scope

The controversial issue of disposing municipal sewage sludge on arable farmland and growing demand on derived fuels could result in a total or partial abandoning of sludge recycling as fertiliser. Alternative disposal strategies like incineration will cause complex changes. A material flow management framework is used to determine the economic-organisational consequences for public authorities, farmers, rural contractors, disposal firms, and population in Schleswig-Holstein.

Methods and Focus

The study is based upon network analysis, analysis of agricultural and wastewater statistics and interviews. After structuring the disposal process, transaction are used to derive costs of different disposal strategies. The purification technique of sewage plant and application of metal salts for precipitation affect the fertilising quality of sludge. Therefore, all plants are classified into 4 different technical groups with decreasing fertilising effect. Now, the amount of sludge and corresponding fertilising benefit is calculated both state wide and for typical farms. Finally costs of different disposal strategies are derived.

Results

Referring to sewage plants sludge disposal in Schleswig-Holstein is characterised by a local structure since less than 10% of all 841 sewage plants produce almost the entire sludge where as many small plants especially in rural areas produce only little amounts. Usually enriched with lime, dewatered sludge fulfilling legal limits is used as organic fertilizer. The number of transactions indicates the costs.

Discussion

To reduce transaction costs, disposal firms try to offer high quantities of sludge to a limited number of farmers. Due to purification technique, the fertilising effect of half the amount of total sludge is reduced. Compared to the total demand on phosphorous, sludge can only substitute up to 4% of phosphorous. Farmers can substitute up to 50% of mineral fertiliser and increase marginal income per hektare. Although changing disposal strategy to incineration would double economic costs, fee for wastewater would remain almost constant.

Conclusions

Small wastewater plants, farmers and rural contractors would be particularly affected by ceasing sludge disposal. Small wastewater plants would have to invest in dewatering equipment, rural contractors would lose an important market segment and farmers (only a small percentage of all farmers uses sludge) would lose additional income. Changing waste management from sludge disposal with many involved parties to e.g. incineration would considerably reduce transaction costs for authorities. In case of partly changing waste management strategy, whereas sludge of small plants could be recycled, the authorities would still have to plan and control the disposal process even for small quantities of sludge. Transaction costs do not decrease proportionally to the decreasing amount of sewage sludge.

Perspectives

Quality management systems initiated by disposal firms should increase the acceptance and prevent a ban of sludge recycling. Nevertheless, the waste market develops from material to energetic use of waste. Significant resources will be lost without a phosphorous recovering from sludge as well as from other organic waste.  相似文献   

2.
3.
A number of products, such as washing agents or pharmaceuticals, enter the hydrosphere mainly with municipal wastewater. In this case the predicted environmental concentrations (PEC) of substances are largely determined by their elimination in municipal wastewater treatment plants and by the dilution ratio of wastewater in the rivers. In this article some rough estimates of the wastewater ratio in German rivers are presented and as a starting point for a more complex model for calculating the PEC more exactly, data on the fluctuation of river flow rates are shown.  相似文献   

4.
5.
Diphenylamine (DPA), the simplest secondary aromatic amine, is a compound from the third European Union (EU) list of priority pollutants. It was assigned to Germany to assess and control its environmental risks. DPA is most commonly used as a stabilizer agent in nitrocellulose-containing explosives and propellants, in the perfumery, and as an antioxidant in the rubber and elastomer industry. DPA is also widely used to prevent the post-harvest deterioration of apple and pear crops. It is a parent compound of many derivatives which are used for the production of dyes, pharmaceuticals, photography chemicals and further small-scale applications. At the beginning of the eighties, the estimated world production of DPA was ?40,000 tons per year (in Germany ?4,000 tons per year). The compound is still produced world-wide by the chemical industries. Recently published reports showed that DPA was found in soil and groundwater (within the ppb to ppm range). Some ecotoxicological reports demonstrated the potential hazard of various diphenylamines to the aquatic environment and to bacteria and animals as well. Studies on the biodegradability of DPA and its derivatives are very sparse. Therefore, further investigations are required to determine the complete dimensions of the potential environmental hazard and to introduce possible (bio)remediation techniques for sites that are contaminated with this compound or its derivatives. This review summarizes the environmental relevance of DPA as has been published in the literature thus far. It may possibly support the German authorities in their assessment of the risks of this priority pollutant.  相似文献   

6.
7.
The quality of regionalizations can only be evaluated with regard to its specific purposes. In environmental monitoring, regionalizations, besides being an analysis tool, has a great importance on the selection of monitoring sites. The article describes the relationship between regionalization, selection procedure and representativeness using the example of Ecological Area Sampling (EAS) and presents the regionalization which was tested in an EAS pilot study.  相似文献   

8.
9.
The azaarenes and the structurally analogous PAH accompany each other and occur ubiquitously in nature. Photochemical conversions like direct photolysis or the photoreaction with nitrate are important natural degradation reactions of azaarenes. Furthermore, photoreactions with chlorine and bromine radicals can be expected in nature. The reactions generate a large number of oxidized, nitrated and halogenated products with unknown toxicity. In this paper, a first screening of changes is reported in acute toxicity during the course of the photochemical reactions. As test system luminescent bacteria are used. For quinoline, isoquinoline and phthalazine the investigations show different changes of the toxicity of the reaction mixtures in dependence on the respective reaction type. The toxicity of the reaction mixtures of quinazoline and quinoxaline increases in all reactions investigated. Furthermore the reactions of bromine radicals with azaarenes also show an increase of the toxicity in all cases. Compared with the azaarenes in all reactions products with significantly higher toxicity are formed.  相似文献   

10.
11.
PEPC-Aktivität     
The criteria currently used to determine the extent of novel forest decline areleaf loss andyellowing of leaves. However, these criteria have only a limited value for indicating damage of woody trees, especially the early stages. Therefore, physiological-biochemical parameters will be useful to measure the extent of forest decline. Results from several natural spruce stands indicate that in needles with early signs of damage and needles with severe damage PEPC activity is significantly higher than in needles of healthy plants. Therefore, PEPC activity can reveal beginning damage and may be used as abiochemical indicator for damage assessments of spruce. The influence of air pollutants on PEPC activity in spruce needles was measured in fumigation chambers and open-top chambers; PEPC activity was shown to be affected by long-term exposition only.  相似文献   

12.
13.
14.
Background, aim, and scope Polycyclic aromatic hydrocarbons (PAH) result from incomplete combustion of almost every organic materials, e.?g. due to forest fires, residential heating, combustion engines, grilling, or smoking. PAH are predominantly distributed over the air-path. Their usage in products (e.?g. moth-balls) has been limited strictly or completely forbidden in the past. In the context of the EU Water Framework Directive (WFD), the single substances anthracene, fluoranthene and naphthalene, as well as PAHs as group of substances, are listed as “priority” substances. Background of this work is a first compilation of sources of PAH emissions, and in this context, the collection of all relevant data and information to calculate the total emissions into surface waters in Germany. Materials and methods Within the scope of diverse research projects, funded by the German Environmental Agency, the available data material concerning PAH input in surface waters has been analyzed by the Fraunhofer Institute for Systems and Innovation Research. On the basis of the collected data, a first evaluation of relevance of the different sources has been conducted using the model MONERIS. Results As a result of the atmospheric deposition, PAHs enter, to a large extent, surface waters directly or indirectly through surface runoff (e.?g. urban areas, wastewater treatment plants, erosion). Discussion Although there is still additional research need for some of the covered PAH sources, a noticeable distribution pattern of relevance emerges. Conclusions The scenarios, based on the currently known sources, show that the implementation or the neglect of emission reduction measures in the field of diffuse air-borne PAHs are crucial for the further development of the deposition of PAHs in surface waters. More far-reaching studies are necessary, e.?g. concerning emissions from inland navigation/motor boats, the inhomogeneous source “products”, or the path “erosion”. Recommendations and perspectives According to the EU-WFD, all depositions, emissions and losses of “priority hazardous” classified substances, such as the group of PAHs, have to be stopped or gradually finished in the long term. Until the year 2015, environmental quality standards (EQS) have to be met for all “priority substances”. Presently, the EQS often are not completely fulfilled for many substances of the PAH group, including benzo(a)pyrene. Reduction measures are necessary within diverse areas, especially concerning diffuse atmospheric emissions (e.?g. “residential heating”).  相似文献   

15.
Humic substances are an important component of organic carbon in natural waters. Their character and properties are determined by the sources and the processes of their origin. Humic substances are not exclusively refractory compounds, but they are involved in several transformation processes in the water. It is not possible to directly analyze humic substances, therefore several methods were applied for their characterization. The presented LC-OCD-technique is a size-exclusion-chromatography with online UV- and carbon detection. Carbon fractions, e.?g. humic substances were differentiated by their molecular size. The portion of humic substances in sediment porewaters of the rivers Elbe, Rhine, Danube, Oder, Müritz-Elde-Waterway was determined. With only a few exceptions it ranges from 50 to 67?% of the dissolved organic carbon. The high molecular weight fraction accounts for 10 to 34?%, and the fraction of the low molecular weight substances was from 7 to 37?%. The ratio between the spectral absorption coefficient (254?nm) and the organic carbon is called SUVA (L/mg × m) and is an inidicator of the proportion of unsaturated bonds in the humic substances. Both high molecular herbal components (e.?g. cellulose, lignin) and biological degradiation products (e.?g. amino acids, sugar) are involved in sediment porewater transformation and degradiation processes. This demonstrates the distribution of the dissolved organic carbon between the fractions.  相似文献   

16.
17.
The stability of H+, NH 4 + , and PO 4 3? ions in rainwater samples was in vestigated under different conditions cf storage and transport. Microbiological and physicochemical processes account for changes. Suppression of microbiological activities in deposition networks using conventional analyses may be achieved by adding AgCl-powder and by cooling to +4 °C.  相似文献   

18.

Aim and Scope

This study was aimed at evaluating environmental effects of tar-oil impregnated (tanalized) tree stakes using simple and efficient biotests to obtain results of its ecological impacts during the tar-oil breakdown in the stake.

Results

  1. Soil respiration was measured in-situ as an indication of soil microbial activity in two field trials. Soil respiration was measured in a 20 year-old apple orchard at various distances from the tar-oil impregnated tree stakes and also on soil mixed with chippings from pine stakes with tar-oil impregnation of different ages.
  2. Cress germination tests were employed to evaluate tar-oil phytotoxicity in a field and laboratory trial. Cress was seeded close to tree stakes in the same 20 year-old apple orchard and germination rates related to tar oil-impregnation. Cress was also seeded in trays in sand mixed with pine chippings from stakes with tar-oil impregnation of different ages.
  3. The portion of the carcinogenic benzoapyrene (BaP) ranged between 0.0015% in freshly tar-oil impregnated to 0.4% in tar-oil impregnated 20-year old trees stakes, i.e. irrespective of the overall PAK concentration and its degradation.
  4. Kinetic analysis using DIXON plots showed a 50% breakdown of overall PAHs after ca. 2.7 years, i.e. km or Ki values of less than 3 years.

Conclusion

Germination tests of cress and endogenous seeds as well as soil respiration proved sensible indicators of the phytotoxicity and ecotoxicity of tar-oil impregnated tree stakes in fruit orchards. Soil respiration proved particularly sensitive to tar-oil ageing. Its combination with kinetic inhibition models resulted in parameters suitable for the interpretation of results.  相似文献   

19.
For a risk assessment of wastes, fast and sensitive screening methods are required to detect possible toxic effects. In this study, different leachability methods (DIN 38414, part 4; EPA 1310; EPA 1320) were used to prepare aqueous leachates from different wastes; these leachates were rested in different bacterial toxicity test systems for possible toxic effects. As bacterial toxicity tests, the luminescent bacteria test and the growth inhibition test with activated sludge bacteria were used. The test systems showed a good agreement of the results from the different leaching methods, thereby indicating the reliability of the test systems used. The luminescent bacteria inhibition test showed a higher sensitivity than the growth inhibition test which is in good accordance with literature data. We conclude that both test systems are well suited to assess the toxic potential of aqueous waste leachates.  相似文献   

20.

Goal and Scope

The constant increase of traffic and the rising energy and material consumption both in industry and trade as well as in private households mean a constant challenge to environmental protection and to the air pollution control. With the commencement of the Federal ambient pollution control act in April 1974, the legal basis for the monitoring of air pollution was created. In future, the limit values laid down in the Council Directive 1999/30/EG, 2000/69/EG and 96/62/EG, will be valid. In town and regional planning there is a great demand for a simple index to evaluate the air quality. From the available data of PM10, NO2, O3, CO, SO2, trends of the air quality will be derived.

Methods

The indices LQI and TLQ suggested by Mayer et al. (2002) were calculated for selected stations of the air pollution monitoring network (ZIMEN) in Rhineland-Palatine. All analysis are based on hourly recorded value, Mean values and frequency distributions are used for the interpretation. Furthermore, the characteristics and trends of the indices under different weather conditions were examined and discussed.

Results

The examination figures out that the air pollutions indices at all stations show similar patterns in the period between January 2001 and December 2002. Neither the LQI, nor the TLQ shows an annual variation. Existing variations are mainly controlled by the general weather situation and the air temperature. High values of the indices appear at extremely high or low mean daily air temperature. The absolute value of the air pollution index is determined by local pollution factors.

Outlook and Recommendations

Both indices are well suitable to evaluate the air quality and to assess the effects of state-aided measures for air pollutant control. Therefore, the indices TLQ and LQI should be published as an additional information in the world wide web.  相似文献   

设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号